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Mushtaq W, Shakeel A, Mehdizadeh M, Alghamdi S. A, Hakeem K. R. Impact of Plant Invasions on Local Vegetation: An Indian Perspective. Biosci Biotech Res Asia 2019;16(4).
Manuscript received on : 18/10/2019
Manuscript accepted on : 27/12/2019
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Impact of Plant Invasions on Local Vegetation: An Indian Perspective

Waseem Mushtaq1, Adnan Shakeel2, Mohammad Mehdizadeh3Sameera A. Alghamdi4,5  and Khalid Rehman Hakeem4,5 

1Alleopathy laboratory, Department of Botany, Aligarh Muslim University, Aligarh, India 202002

2Environmental section, Department of Botany, Aligarh Muslim University, Aligarh, India 202002

3Department of Agronomy and Plant Breeding, University of Mohaghegh Ardabili, Ardabil, Iran

4Department of Biological Sciences, King Abdulaziz University, Jeddah, 21589, Saudi Arabia

5Center for Excellence Research in Biotechnology, King Abdulaziz University, Jeddah, Saudi Arabia

Corresponding Author E-mail: kur.hakeem@gmail.com

DOI : http://dx.doi.org/10.13005/bbra/2792

ABSTRACT: Invasive species are key operators of worldwide ecological change causing the loss of biodiversity, modifying structure and functioning of bio-system, and disturbing establishment of ecosystem amenities throughout the world. About 8.6% of the overall flora of India is alien. A considerable rise in worldwide trade and travel is expected to accelerate entry, spreading and eventual establishment of foreign species in India. Whereas the systematic catalogue of non-native species incarnates the primary vital stage, however, more comprehensive investigations on description of alien species in India, study of their potential invasion environments, recognition of possible ways of invasion and their impact on local vegetation are still missing. The present study reports the incidence of 173 species of alien flora in India, their origins from different parts of the globe belonging to a diverse array of families with an emphasis on the adverse effect of important invasive species on the local vegetation so as to generate an understanding of plant invasions and develop policy framework for their management.

KEYWORDS: Ecosystem; Invasive species; Management

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Introduction

Invasive plants are the ones that have been deliberately or unintentionally brought to regions other than their natural habitats and cause serious implications to economy, environment, vegetation and humans in the invaded areas. These plants expand rapidly and threaten the local vegetation by competing for water, space and nutrients. The invasive species modify the light, temperature and solar radiation availability in the invaded area. The access to food, shelter, and relaxing sites are modified for many animals as well. This can result in variations in local vegetation, rate of recurrence of fires, nutrient cycling, water accessibility and soil structure. However, a few cases have reported benefits of invasive plants. 1, 2, 3 For instance, they can offer fire wood to local people or supplement resources for native animal species. However, these advantages do not outperform the negative impacts. Intrusive plants affect local species through complex interactions and routes. Lest these aspects are appropriately comprehended, it is hard to foresee what kind of effect invasive plants will have.

The global annual damage from invasive alien species (IAS) in different parts of the world has been assessed $30 billion in USA4, €12 billion in Europe5, and US $14 billion in China6. In perspective of these environmental and financial effects of IAS, a resolution on biodiversity in Nagoya, Japan (2010) implemented the tactical proposal for biological diversity 2011-20 for IAS identification and recognition of their pathways were prioritized and measures were encouraged to counter their introduction and establishment.

As in many other countries, alien plants7 have also plagued India and its magnitude will further intensify because of expanding Indian economy. Actually, the size of stock imports is a critical determining factor of the extent of IAS8 in addition to the frequency of introduction of foreign species. Being a rich mega-biodiverse land, the implications of IAS on the preservation and sustainable usage of biodiversity would be quite articulated in India. Henceforth, there is an immense requirement to construct an integrated structure for the forecast, anticipation, fast reaction and control of alien plant intrusions in India. The present review addresses characteristics of invasive species, recognizes 173 IAS in India and gives the impact of few important alien plants (Lantana camera L., Parthenium hysterophorus L., Nicotiana plumbaginifolia Viv. and geratum conyzoides L.) on local vegetation.

Distinctive characteristics of Invasive species

Invasive species have trademark characteristics in diverse soil types and different environmental setups. These are generalist in distribution, avoided by grazing animals, abundance in poor soils as the interspecific competition has been removed due to selective grazing of other native grasses, short life cycle, high reproductive input, high dispersal rates, produces small and light weighted seeds that could be dispersed easily by winds providing them with the advantages of exploring more long habitats9, broad and abundant native range. IAS usually contain comparatively little amounts of genetic material in their cell nuclei10. Evidently, their cells undergo quick mitosis and duplicate rapidly and subsequently the whole plant can develop briskly as compared to other plants with greater genomic content. It provides a massive advantage to IAS in distressed landscapes.

Invasive plants in India

The World Conservation Monitoring Centre (WCMC) recognizes 1,604,000 plant species worldwide and India shares 8% of it.  A total of 15000 angiospermic plants are found in India, out of which 4900 are native, i.e. only 33%11. Hajra and Mudgal12 have reported 5400 endemics out of a total of 17000 angiospermous plants of India. India is an essential focal point of the world agriculture as it has given 167 species to the mankind and has been home to 320 wild crop species. The current review has focused on 173 IAS in India (Table 1). These species are the etremee stubborn invasive plants of a diverse array of families as Mimosacceae, Asteraceae, Amaranthaceae, Papilionaceae, Solanaceae, Convolvulaceae and others.

Table 1: Invasive alien plants in India.

Family Botanical name Habit Origin
Acanthaceae

 

Peristrophepaniculata (Forssk.) Brummitt Herb

 

Tropical America

 

Ruelliatuberosa L. 
Amaranthaceae

 

Digeramuricata (L.) Mart.  Herb

 

South-West Asia
Celosia argentea L. Tropical Africa
Alternantheraparonychioides A. St. Hil Tropical America

 

Alternantheraphiloxeroides (Mart.) Griseb
Alternantherapungens Kunth
Alternantheratenella Colla
Gomphrenaserrata L.
Apocynaceae Catharanthus pusillus (Murray) Don Herb Tropical America

 

Arecaceae Borassusflabellifer L.

 

Tree Tropical Africa
Araceae Pistiastratiotes L.  Herb Tropical America

 

Asclepiadaceae

 

Cryptostegiagrandiflora R. Br. Herb

 

Madagascar
Asclepiascurassavica L.  Tropical America
Calotropisgigantea (L.) R.Br.  Shrub Tropical Africa

 

Calotropisprocera (Ait.) R.Br.
Asteraceae Echinopsechinatus Roxb.  Herb

 

Afghanistan
Glossocardiabosvallea (L. f.) DC. East Indies
Sonchus asper Hill Mediterranean

 

Sonchusoleraceus L.
Dicomatomentosa Cass. Tropical Africa
Ageratinaadenophora (Spreng.) King & Robinson Tropical America

 

Ageratum conyzoides L.
Ageratum houstonianum Mill.
Bidenspilosa L.
Blainvilleaacmella (L.) Philipson
Blumeaeriantha DC. 
Blumealacera (Burm.f.) DC.
Blumeaobliqua (L.) Druce
Chromolaenaodorata (L.) King & Robinson
Conyzabipinnatifida Wall.
Crassocephalumcrepidioides (Benth) Moore
Emilia sonchifolia (L.) DC. 
Ecliptaprostrata (L.) Mant. 
Galinosogaparviflora Cav. 
Gnaphaliumcoarctatum Willd.
Gnaphaliumpensylvanicum Willd.
Gnaphaliumpolycaulon Pers. 
Grangeamaderaspatana (L.) Poir.
Flaveriatrinervia (Spreng.) C. Mohr. Tropical Central America

 

Lagasceamollis Cav. 
Tridaxprocumbens L. 
Parthenium hysterophorus L. Tropical North America
Spilanthesradicans Jacq.   Tropical South America

 

Xanthium strumarium L.
Youngia japonica (L.) DC.
Youngia japonica (L.) DC.
Mikaniamicrantha Kunth Climber Tropical America
Synedrellanodiflora (L.) Gaertn. Herb West Indies
Balsaminaceae Impatiens balsamina L. Herb

 

Tropical America

 

Brassicaceae

 

Cardaminehirsuta L. 
Cardaminetrichocarpa Hochst. ex A.Rich.
Rorippadubia (Pers.) Hara
Cactaceae Opuntiastricta (Haw.) Haw. Herb Tropical America

 

Caesalpiniaceae Cassia absus L.  Herb Tropical America

 

Cassia alata L. Shrub West Indies
Cassia hirsuta L. Herb Tropical America
Cassia obtusifolia L.
Cassia occidentalis L. Tropical South America
Cassia pumila Lam. Tropical America

 

Cassia pumila Lam.
Cassia rotundifolia Pers. Tropical South America

 

Cassia tora L.
Cassia uniflora Mill.
Cleomaceae

 

Cleome monophylla L. Herb

 

Tropical Africa
Cleome gynandra L. Tropical America

 

Cleome rutidosperma DC. 
Cleome viscosa L.
Convolvulaceae

 

Euphorbia heterophylla L. Herb Tropical America

 

Evolvulusnummularius (L.) L. 
Ipomoea carnea Jacq. 
Ipomoea eriocarpa R. Br. Tropical Africa
Ipomoea hederifolia L.  Tropical America

 


Ipomoea obscura
 (L.) Ker.-Gawl.
Tropical Africa
Ipomoea pes-tigridis L. Tropical East Africa
Ipomoea quamoclit L. Tropical America

Tropical America

 

Merremiaaegyptia (L.) Urban. 
Ipomoea staphylina Roem. &Schult.  Tropical Africa
Cyperaceae

 

Cyperusdifformis L. Herb Tropical America
Cyperusiria L.
Fuirenaciliaris (L.) Roxb.
Euphorbiaceae

 

Chamaesyce hirta (L.) Millsp. Herb

 

Tropical America

 

Chamaesyceindica (Lam.) Croizat Tropical South America
Chrozophorarottleri (Geis.) Spreng. Tropical Africa
Croton bonplandianum Boil.  Temperate South America
Euphorbia cyathophora Murray Tropical America

 

Phyllanthustenellus Roxb. Mascarene Islands
Synadeniumgrantii Hook. f. Tropical America
Lamiaceae Poit.  Leonotisnepetiifolia (L.) R.Br. Herb

 

Tropical Africa
Hyptissuaveolens (L.) Tropical America

 

Ocimumamericanum L.
Liliaceae Asphodelustenuifolius Cav. Herb Tropical America
Malvaceae Malachracapitata (L.) L. Herb

 

Tropical America

 

Malvastrumcoromandelianum (L.) Garcke
Sidaacuta Burm. f. 
Urenalobata L. Tropical Africa
Melastomataceae Clidemiahirta (L.) D. Don Herb Tropical America
Mimosacceae Acacia mearnsii De Wild.

 

Tree

 

South-East Australia
Acacia farnesiana (L.) Willd. Tropical South America
Leucaenaleucocephala (Lam.) de Wit  Herb Tropical America

 

Mimosa pigra L. Shrub

 

Mimosa pudica L.
Prosopisjuliflora (Sw.) DC. Herb Mexico
Nyctaginaceae Mirabilis jalapa L. Herb

 

Tropical America

 

Onagraceae

 

 Ludwigiaadscendens (L.) Hara 
Ludwigiaoctovalvis (Jacq.) Raven  Tropical Africa

 

Ludwigiaperennis L.
Oxalidaceae Oxalis corniculata L. Herb Europe
Papaveraceae Argemonemexicana L.  Herb

 

Tropical Central & South America
Papilionaceae

 

Aeschynomeneamericana L. Herb

 

Tropical America

 

Crotalaria pallida Dryand
Crotalaria retusa L.
Cytisusscoparius (L.) Link Europe
Indigoferaastragalina DC. Tropical America
Indigoferaglandulosa Roxb. exWilld. 
Indigoferalinifolia (L.f.) Retz. Tropical South America
Indigoferalinnaei Ali Tropical Africa

 

Indigoferatrita L.f.
Stylosantheshamata (L.) Taub. Tropical America

 

Ulexeuropaeus L.  Shrub Western Europe
Macroptiliumatropupureum (DC.) Urban Climber

 

Macroptiliumlathyroides (L.) Urban Tropical Central America
Melilotus alba Desv.  Herb Europe
Sesbaniabispinosa (Jacq.) Wight  Shrub

 

Tropical America

 

Echinochloacolona (L.) Link  Herb

 

Tropical South America

 

Echinochloacrusgalli (L.) Beauv. 
Imperatacylindrica (L.) Raensch. Tropical America

 

Pennisetumpurpureum Schum.
Rhynchelytrumrepens (Willd.) C.E. Hubb.
Saccharumspontaneum L.  Tropical West Asia
Passifloraceae Passiflorafoetida L. Herb Tropical Sourth America
Pedaliaceae

 

Martyniaannua (Houstoun&Martyn) L.  Herb

 

Tropical America

 

  Pedalium murex L. 
Piperaceae Peperomiapellucida (L.) Kunth Herb Tropical Sourth America
Pontederiaceae

 

Eichhorniacrassipes (C. Martius) Solms-Loub. Herb

 

Tropical America

 

Monochoriavaginali(Burm. f.) C. Presl. 
Portulacaceae

 

Portulacaoleracea L. Herb

 

Tropical South America
Portulacaquadrifida L. Tropical America

 

Rubiaceae Spermacocehispida L. Herb Tropical America

 

Salviniaceae Salviniamolesta D. S. Mitch. Herb Brazil
Scrophulariaceae Mecardoniaprocumbens (Mill.) Small Scrophulariaceae Herb

 

Tropical North America
Scopariadulcis L. Tropical America

 

Toreniafournieri Linden ex E. Fournier Australia
Solanaceae Daturainnoxia Mill.  Shrub

 

Tropical America

 

Daturametel L. Tropical America

 

Nicotiana plumbaginifolia Viv. Herb Tropical America

 

Physalisangulata L. 
Physalispruinosa L.
Solanumamericanum Mill.
Solanumseaforthianum Andrews Climber Brazil
Solanumtorvum Sw.  Shrub

 

West Indies
Solanumviarum Dunal Herb Tropical America

 

Tiliaceae Corchorustridens L.  Herb Tropical Africa
Corchorustrilocularis L.
Triumfettarhomboidea Jacq.  Tropical America

 

Corchorusaestuans L.
Corchorusfascicularis Lam.
Turneraceae Turnerasubulata J. E. Smith  Herb Tropical America

 

Typhaceae Typhaangustata Bory. and Choub. Herb

 

Tropical America

 

Urticaceae Pileamicrophylla (L.) Liebm. Herb Tropical Sourth America
Verbenaceae

 

Lantana camara L. Herb

 

Tropical America

 

Stachytarphetajamaicensis (L.) Vahl
Stachytarphetaurticaefolia (Salisb.) Sims
Zygophyllaceae Tribuluslanuginosus L. Herb

 

Tropical America

 

Tribulusterrestris L.


Selected Problematic Invasive Weeds in India

Lantana camera L.

Lantana camera L. is a member of Verbenaceae family well known for its invasive nature and is considered among the world’s top 10 worst weeds. In India, it was introduced at the beginning of 19th century. Since its invasion to India, it has created a major problem to native flora of many states. L. camera has flourished in plains of India as well as is Himalayan regions13. Due to its allelopathic action it causes a serious threat to native vegetation. It contains several allelochemicals viz: phenolics, methylcoumarin, umbelloferone and salicylic acid. Among all these allelochemicals, salicylic acid is the most phytotoxic14. A recent report claims the occurrence of toxic allelochemicals in Lantana14. L. camera shows a significant effect on seed germination and growth of native vegetation15, 16, 17.

Parthenium hysterophorus L.

Parthenium hysterophorus L. is a member of Asteraceae family, also known as congress grass is considered among 100 most invasive species in the world. In more than 40 countries, it is regarded as an obnoxious weed of field crops18. It has entered India accidently through conjugation with imported food from the USA between the period of 1950s to 1960s19. Its presence was first detected in Pune, Maharashtra (1955). After that it was delineated taxonomically by Rao in 195619. It has the potential of quick colonization with several other characteristics, such as wide adaptability, less number of natural niche enemies, drought tolerance, prolonged viability of seeds, high production of seeds, seeds with small size and light weight, long dispersal of seeds through air, water, birds and other carriers, strong competition and allelopathy makes it a successful invader of crop fields18.  Besides that, it is also capable of causing human health problems like skin allergies, irritation of eyes with mild fever. It is unappetizing and harmful to farm animals. Various allelochemicals have been extracted from the roots, stem, leaves, inflorescence, spores and seeds. These include soluble phenolics and sesquiterpene lactones. The occurrence of plant growth suppressors in P.hysteriphorus was first reported by Rajan20 and Kanchan21.  Along with Parthenin, other inhibitors such as caffeic acid and p-coumaric acid were also found in the stem21 of this weed. The leaf leachates of P. hysterophorus show inhibitory effects on several agricultural and tree crops22, 23.

Nicotiana plumbaginifolia Viv.

Nicotiana plumbaginifolia Viv. (Solanaceae family) a native of Cuba, South America and Caribbean is reported as a weed of wastelands and cultivated lands. It is considered as an agricultural weed as well24. It is invasive in India and is regarded as an aggressive colonizer25. This herbaceous plant also has some medicinal values26. The allelochemicals isolated from its leaves are hexamethoxy 4′,5′ methylenedioxyflavone, exoticin, dimethylenedioxy 3,5,3′trimethoxyflavone and hexamethoxy 6,7 methylenedioxyflavone. Mushtaq et al.25, 28 found the plant has serious growth inhibitory properties on other plants. Mushtaq and Siddiqui29 have reported the negative growth effects of other members of Solanaceae family as well.

Ageratum Conyzoides L.

Ageratum conyzoides L. is a member of Asteraceae family is reported as a noxious weed in agricultural fields and a colonizer of open degraded lands. It is native to South and Central America30. It also serves as a host to pathogens including nematodes thus, affects crops31. Soon after its invasion on land, it suppresses the local vegetation causing inadequacy of fodder. Its invasion to forests critically threatens many of essential medicinal and aromatic plants. A. conyzoides was identified in India before 188232. Ageratum has been reported to suppress growth and yield of native crop species through the release of various phenolics and volatile oils33. Besides its effect on crops, it also affects human health due to its strong pungent odor. Nausea, allergy and giddiness are some of the health problems caused by this weed in humans.

Role of floods in plants invaions.

Researchers believe that the prevalence of invasive plants is one of the most important environmental problems in Kerala India. Particularly after the floods, the prevalence of invasive plants in this area has increased. Seasonal flooding has a direct effect on plant invasion to new environments34. Many plant species inhabiting mountain regions enter the plains and agricultural ecosystems through flood flows, and some of these species have a high potential for conversion into invasive weed species. These plants due to their specific biological, morphological and physiological characteristics and high adaptability to climatic conditions, has potential to rapidly grow and reproduction in new environments and compete with crops as invasive weeds35. Shafroth et al.36 evaluated the importance of flood events on the establishment of weeds and found that Saltcedar (Tamarix ramosissima) have potential to establish in new lands after floods. Floods can be considered as a seed carrier of plant species37 which often transmits the seeds of invasive species to new environments depending on their biological status38. Cuda et al.39 studied the effects of floods on weed invasion in Europe regions and reported Impatiens glandulifera as an invasive weed due to floods and spreading through river corridors.

Management

Generally, the management of prolific invasive plant species is one of the most important agricultural and environmental challenges in India. These plants have potential for threaten ecosystems, capture the ecological niches in agricultural systems, and cause many problems in agricultural production. Therefore, it is very important to prevent the establishment and effective management of these plants. In order to prevent the entrance and establishment of invasive plants in new environments, all processes related to the import of seeds and reproductive organs of new plants, planting and transfer of plants in new areas should be carefully monitored and prevented from introduction of suspected plant species. Where preventive strategies are not successful, the rapid detection of areas occupied by these plants and complete eradication in the early stages of their establishment is very important. In the case of established invasive plants, preventing the distribution and transmission of seeds and reproductive organs can lead to manage the development of plant invasion. Srivastava et al.16 reported 149 invasive plants from North-Eastern Uttar Pradesh, India, and concluded that early identification and reporting of infestation and spread of these plants is very important for their effective management. Biological control method is one of the most effective methods for managing invasive plant species. The most important advantage of the biological control method for invasive plant species is that, after the establishment of biological control agents, a sustainable and long-term management of invasive species is achievable. Wheeler et al40 reported biological control as a successful method for management of invasive weed Schinus terebinthifolia.

Conclusions

Invasive species form the second most serious threat to biodiversity after habitat destruction. Some invasive weed species make a dramatic impact on the processes of ecosystems and biodiversity when they invade. Invasion of an alien species is habitat-dependent. Generally the habitats that are nutrient-rich witness more conquest as compared to poor habitats. High reproductive potential, short life cycle and production of many seeds/propagules are some characteristic traits associated with successful invaders. Our analysis summarises the evidences for the impact of alien plant species on many ecological variables. Recently, the negative effects of alien species on resident crops and the mechanisms for these effects have attracted the focus of researchers. The decrease in local plant species due to invasive species and their development was the main focus of this review.

From the available literature it becomes evident that invasive species have both positive as well as negative impacts. This dual cost nature of many invasive species creates conflict of interests among stakeholders. Therefore, during the management of invasive alien species a uniform management policy cannot be adopted. The invasion of many weed species harmed Indian native flora e.g. Lantana camara invasion to India proved dreadful. Currently this invasive weed occupies 13 million hectares of land and further continues to expand its establishment because of its high invasive potential. The control of these invasive weeds may help in protection and restoration of biodiversity. Because of the fast economic globalization and increased trade with other countries, India has become a good recipient for alien invasive species. There is a need to inventorize the alien flora of India so that the research on invasion biology can be geographically understood. These inventories will act as scientific baselines to understand the pattern, impact and management of invasive plant species in India.

Acknowledgement

Authors are thankful to the Aligarh Muslim University, Aligarh, India; for their support in the collaboration of this project.

Conflict of interest

We declare there is no conflict of interest among us.

References

  1. Chapman P. M. (2018). Negatives and Positives: Contaminants and Other Stressors in Aquatic Ecosystems. Bulletin of Environmental Contamination and Toxicology, 100(1):3-7.
  2. Rejmankova E., Sullivan B. W., Ortiz Aldana J. R., Snyder J. M., Castle S. T. and Reyes Morales F. (2018). Regime shift in the littoral ecosystem of volcanic Lake Atitlán in Central America: combined role of stochastic event and invasive plant species. Freshwater Biology, 63(9):1088-1106.
  3. Quijon P. A., Tummon F. P. and Duarte C. (2017). Beyond negative perceptions: The role of some marine invasive species as trophic subsidies. Marine Pollution Bulletin, 116(1-2):538.
  4. Pimentel D., Zuniga R. and Morrison D. (2005). Update on the environmental and economic costs associated with alien invasive species in the United States. Ecol Econ 52:273–288.
  5. Kettunen M., Genovesi P., Gollasch S., Pagad S., Starfinger U., ten Brink P. and Shine C. (2008). Technical support to EU strategy on invasive species (IS)—assessment of the impacts of IS in Europe and the EU (Final module report for the European Commission). Institute for European Environmental Policy (IEEP): Brussels, pp40 ?Annexes, May 2008 (DG ENV contract).
  6. Xu H. G., Ding H., Li M.Y., Qiang S., Guo J. Y., Han Z. M., Huang Z. G. Sun H. Y., He S. P., Wu H. R. and Wan F. H. (2006). The distribution and economic losses of alien species invasion to China. Biological Invasions, 8:1495-1500.
  7. Goyal A. K., Arora S. (2009). India’s Fourth National Report to the convention on biological diversity. Ministry of Environment and Forests, Government of India, New Delhi.
  8. Roques A., Rabitsch W., Rasplus J. Y., Lopez-Vamonde C., Nentwig W., Kenis M. (2009). Alien terrestrial invertebrates of Europe. In: DAISIE handbook of alien species in Europe. Springer, Dordrecht, Pp. 63-79.
  9. Gairola S., El-Keblawy A. and Mahmoud T. (2016). A note on the current distribution of Nicotiana plumbaginifolia (Solanaceae) in the United Arab Emirates. National Academy Science Letters, 39(6):461-464.
  10. Randall J. M. and Marinelli J. (1996). Invasive plants: weeds of the global garden. Brooklyn Botanic Garden Club, Handbook Number 149.
  11. Nayar M.P. (1989). In situ conservation of wild flora resources. Bulletin of the Botanical Survey of India 29:319-333.
  12. Hajra P.K. and Mudgal V. (1997). Plant Diversity Hotspots in India An overview. BSI, Calcutta.
  13. Kohli R. K., Dogra K. S., Batish D. R. and Singh H. P. (2004). Impact of invasive plants on the structure and composition of natural vegetation of northwestern Indian Himalayas. Weed Technology, 18 (sp 1):1296-1300.
  14. Sharma O. P., Sharma S., Pattabhi V., Mahato S. B. and Sharma P. D. (2007). A review of the hepatotoxic plant Lantana camara. Critical Reviews in Toxicology 37 (4): 313- 352.
  15. Nawab N. P. and Yogamoorthi A. (2016). Allelopathic effects of aqueous extract of Lantana camara on seed Germination of black gram Vigna mungo L. Environmental Science: An Indian Journal, 12(11).
  16. Srivastava S., Dvivedi A. and Shukla R. P. (2014). Invasive Alien Species of Terrestrial Vegetation of North-Eastern Uttar Pradesh. International Journal of Forestry Research, Article ID 959875:1-9.
  17. Gantayet P. K., Adhikary S. P., Lenka K. C. and Padhy B. (2014). Allelopathic impact of Lantana camara on vegetative growth and yield components of green gram (Phaseolus radiatus). International Journal of Current Microbiology and Applied Sciences, 3 (7):327-335.
  18. Bajwa A. A., Chauhan B. S., Farooq M., Shabbir A., Adkins S. W. (2016). What do we really know about alien plant invasion? A review of the invasion mechanism of one of the world’s worst weeds. Planta,244(1):39-57.
  19. Kohli R. K., Batish D. R., Singh H. P. and Dogra K. S. (2006). Status, invasiveness and environmental threats of three tropical American invasive weeds (Parthenium hysterophorus , Ageratum conyzoides L., Lantana camara L.) in India. Biological Invasions, 8 (7):1501-1510
  20. Rajan L. (1973). Growth inhibitor(s) from Parthenium Hysterophorus Current Science, 42:729-730.
  21. Kanchan S. D. (1975). Growth inhibitors from Parthenium hysterophorus Current Science 44:358–359.
  22. Singh, S. P. (1991). Allelopathic potential of Parthenium hysterophorus Journal of Agronomy and Crop Science, 167 (3):201-206.
  23. Kohli R. K. and Rani D. (1992). Identification and bioefficacy of soil chemics of Parthenium. In Proccedings of the 1st National Symposium on Allelopathy in agroecosystems, Hisar, India, Februaray (Pp. 196-198)
  24. HEAR (2017). Alien species in Hawaii. Hawaii Ecosystems at Risk. Honolulu, USA: University of Hawaii. http://www.hear.org/AlienSpeciesInHawaii/index.html
  25. Mushtaq W., Quratul-Ain, Siddiqui M. B, (2018) Screening of alleopathic activity of the leaves of Nicotiana plumbaginifolia on some selected crops in Aligarh, Uttar Pradesh, India. International Journal of Photochemistry and Photobiology 2(1):1-4.
  26. Devi A. D., Devi O. I., Singh T. C., Singh E. J. (2014). A study of aromatic plant species especially in Thoubal district, Manipur, North East India. International Jouirnal of Scientific and Research Publications,4:2250-3153.
  27. Shahriar M., Chowdhury S. A., Imam M. Z. and Datta B. K. (2015). Analgesic and Neuropharmacological Activities of Methanol Extract From the Leaf of Nicotiana plumbaginifolia Bangladesh Pharmaceutical Journal, 18(2):85-9.
  28. Mushtaq W., Quratul-Ain, Siddiqui M. B. and Hakeem K. R. (2019). Cytotoxic allelochemicals induce ultrastructural modifications in Cassia tora and mitotic changes in Allium cepaL.: a weed versus weed allelopathy approach. Protoplasma, 256:857-871.
  29. Mushtaq W. and Siddiqui M. B, (2018) (2018). Allelopathy in Solanaceae plants. Journal of Plant Protection Research, 58(1):1-7.
  30. Greuter W. (2016). Occurrence details for Ageratum conyzoides. Compositae (pro parte majore). Euro+Med Plantbase ­ the information resource for Euro­Mediterranean plant diversity [ed. by Greuter, W. \Raab­Straube, E. von].
  31. BioNET-EAFRINET (2016). Invasive plants key and fact sheets. http://keys.lucidcentral.org/keys/v3/eafrinet/index.htm
  32. Stearn W. T. (1965). Grisebach’s flora of the British west Indian islands: a biographical and bibliographical introduction. Journal of the Arnold Arboretum, 46 (3):243-285.
  33. Singh H. P., Batish D. R., Pandher J. K. and Kohli R. K. (2003). Assessment of allelopathic properties of Parthenium hysterophorus Agriculture, Ecosystems and Environment, 95(2):537-541.
  34. Nunes da Cunha C. and Junk W. J. (2004). Year-to-year changes in water level drive the invasion of Vochysia divergens in Pantanal grasslands. Applied Vegetation Science, 7:103-110.
  35. McGeoch M. A., Butchart S. H. M., Spear D., Marais E., Kleynhans E. J., Symes A., Chanson J. and Hoffman M. (2010) Global indicators of biological invasion: species numbers, biodiversity impact and policy responses. Diversity and Distribution,16:95–108.
  36. Shafroth P. B., Clever J. R., Dudley L., Stuart J. and Taylor J. P. (2005). Control of Tamarix in the western U.S.–implications for water salvage, wildlife use, and riparian restoration. Environmental Management, 35:231-246.
  37. Goodson J. M., Gurnell A. M., Angold P. G. and Morrissey I. P. (2003). Evidence for hydrochory and the deposition of viable seeds within winter flow-deposited sediments: the River Dove, Derbyshire, UK. River Research and Applications, 19:317-334.
  38. Schmiedel D. and Tackenberg O. (2013). Hydrochory and water induced germination enhance invasion of Fraxinus pennsylvanica. Forest Ecology and Management, 304:437-443.
  39. Cuda J., Rumlerov Z., Bruna J., Skalova H. and Pysek P. (2017). Floods affect the abundance of invasive Impatiens glandulifera and its spread from river corridors. Diversity and Distributions:1-13. http://dx.doi.org/10.1111/ddi.12524
  40. Wheeler G. S., Mc-Kay F., Vitorino M. D., Manrique V., Diaz R. and Overholt W. A. (2016). Biological Control of the Invasive Weed Schinus terebinthifolia (Brazilian Peppertree): A Review of the Project with an Update on the Proposed Agents. Southeastern Naturalist, 15:15-34.
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